Abstract

The removal mechanisms and extent of degradation of 28 chemicals (triclosan, fifteen polycyclic aromatic hydrocarbons, four estrogens, and eight polybrominated diphenyl ether congeners) in different biological treatment systems [activated sludge, up-flow anaerobic sludge blanket reactor (UASB) and waste stabilization pond (WSP)] was investigated to provide insights into the limits of engineered biological treatment systems. This was done through degradation experiments with inhibition and abiotic controls in static reactors under aerobic and anaerobic conditions. Estrogens showed higher first order degradation rates (0.1129 h−1) under aerobic conditions with activated sludge inocula followed by low molecular weight (LMW) PAHs (0.0171 h−1), triclosan (0.0072 h−1), middle (MMW) (0.0054 h−1) and high molecular weight PAHs (HMW) (0.0033 h−1). The same trend was observed under aerobic conditions with a facultative inoculum from a WSP, although at a much slower rate. Biodegradation was the major removal mechanism for these chemicals in the activated sludge and WSP WWTPs surveyed. Photodegradation of these chemicals was also observed and varied across the group of chemicals (estrogens (light rate = 0.4296 d−1; dark = 0.3900 d−1) degraded faster under light conditions while reverse was the case for triclosan (light rate = 0.0566 d−1; dark = 0.1752 d−1). Additionally, all the chemicals were resistant to anaerobic degradation with UASB sludge, which implies that their removal in the UASB of the surveyed WWTP was most likely via sorption onto solids. Importantly, the first order degradation rate determined in this study was used to estimate predicted effluent concentrations (PECs). The PECs showed good agreement with the measured effluent concentrations from a previous study for these treatment systems.

Highlights

  • Knowledge on the most important mechanisms for micropollutant removal, and the rate of those mechanisms is essential to understand the limits of current wastewater treatment technologies and determine how they might be improved

  • Triclosan Biotransformation of Triclosan With Activated Sludge Inocula Under aerobic conditions, triclosan concentration in the batch tests decreased by 74% over the duration of the experiment (168 h) (Figure 1, Supplementary Figure S1)

  • Degradation of all the chemicals was only observed under aerobic conditions with a faster reaction kinetic with activated sludge inocula over the facultative inocula from the WSP

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Summary

Introduction

Knowledge on the most important mechanisms for micropollutant (chemical contaminants) removal, and the rate of those mechanisms is essential to understand the limits of current wastewater treatment technologies and determine how they might be improved. Biodegradation and sorption have been identified as the main mechanisms of xenobiotic removal in wastewater treatment plants, with volatilization only playing a minor role (Verlicchi et al, 2012). Falas et al demonstrated that biodegradation was the main fate mechanism for a group of ≥20 structurally diverse non-volatile low-sorbing pharmaceuticals in laboratory experiments using unacclimated sludge as an inoculum in different treatment configurations and conditions. There has been relatively little systematic research into the fate and mechanisms of chemicals across different use-classes, especially in the context of microbial inocula from range of real full-scale treatment processes (Falås et al, 2016)

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